On 2020-08-13 06:05:21, user Sarah M wrote:
Response to Etebari et al. 2020 ‘Genetic structure of the coconut rhinoceros beetle (Oryctes rhinoceros) population and the incidence of its biocontrol agents (Oryctes rhinoceros nudivirus) in the South Pacific Islands’ bioRxiv preprint doi: https://doi.org/10.1101/202...
Sean D.G. Marshall, Sarah Mansfield, Trevor A. Jackson <br />
AgResearch, Lincoln Science Centre, Private Bag 4749, Christchurch 8140, New Zealand
Kayvan Etebari and co-authors present genetic data that they contend supports their claims that the recent invasion of coconut rhinoceros beetle (CRB) into new areas of the Pacific was not caused by CRB-G (Marshall et al. 2017). Instead, they argue this invasion process is driven by several genetically distinct groups of CRB. A central plank to their argument is genetic analysis of the invasive CRB population found on Guadalcanal, Solomon Islands. They also present data from several countries on infection rates in CRB populations of the Oryctes rhinoceros nudivirus (OrNV) and hypothesise that OrNV has entered the invaded countries along with the invasive CRB population.
We have serious concerns regarding the methodology used to analyse the data presented by Etebari et al., and their interpretation of the results. Previous attempts to raise these concerns with the lead author and to invite discussion of the findings with the CRB Action Group have been unsuccessful. As it stands, the preprint omits significant methodological information and fails to place their findings in the wider context of CRB invasion into the Pacific. Our concerns can be grouped under three key areas: 1) conflation of two different levels of population structure within CRB, i.e. biotype and haplotype; 2) recent research to address new CRB invasions is not taken into account, particularly in Vanuatu and the Solomon Islands; and 3) failure to prevent cross-contamination leading to artificially high ‘rates of OrNV infection’, which are not substantiated by other published techniques used to detect OrNV infection in CRB.
Below we elaborate on these three points. We invite the authors to contact us directly regarding the concerns raised.
1) conflation of two different levels of population structure within CRB: biotype and haplotype<br />
Marshall et al. 2017 presented genetic data that characterised different populations from the native and invasive range of CRB. In doing so, they identified a genetic marker that distinguished the newly invasive populations from older populations that arose from the initial Pacific invasion by CRB. They also presented bioassay data demonstrating that the new invasive CRB populations were not susceptible to infection by ingestion of the original strain of OrNV that was used to control the initial Pacific invasion of CRB (Huger 2005). Ingestion is the natural route of infection for OrNV so inability to infect new invasive populations is a serious concern for control of CRB. They concluded that there were four clades within the CRB populations they had sampled, with some further subdivision within each of these clades (Fig. 2, Marshall et al. 2017). Three of these clades, while genetically distinct, were all characterised by their susceptibility to the original strain of OrNV used to control the initial CRB invasion in the Pacific. These three clades included native CRB populations and populations from regions affected by the initial CRB invasion and collectively were named CRB-S. The fourth clade included CRB populations from the newly invaded regions (Guam, Papua New Guinea, Hawaii, Solomon Islands) as well as parts of the native range (Philippines, Indonesia). This fourth clade was named CRB-G. Thus, Marshall and co-authors identified two distinct levels of population structure within CRB. The first level (CRB-G and CRB-S) is associated with susceptibility to the original strain of OrNV introduced to the Pacific. The second, more complex, level reflects geographic groupings in the native and invasive range of CRB.
Reil et al. 2018 built on this initial analysis of CRB genetics by investigating the genetic substructure of CRB in more depth, particularly in Palau, where there may have been multiple CRB invasions. They concurred that the new Pacific invasion was correlated with the presence of CRB-G. A key outcome of their paper was the use of the term ‘biotype’, i.e. conspecifics that appear similar but exhibit variation in one or more functional traits, to characterise the CRB-S/CRB-G dichotomy. This is a useful distinction to avoid confusion between this level of population structure, and the more finely divided population structure and haplotypes associated with different geographic regions.
Etebari et al. conflate these two levels of population structure by inserting the PNG haplotype group into the CRB-S/CRB-G dichotomy. A PNG haplotype was identified by Marshall et al. 2017 and placed in Clade II, among the three clades associated with CRB-S. These specimens came from several locations in PNG known to have been affected by the earlier Pacific CRB invasions in the 1940s (Table 2, Marshall et al. 2017). The CRB-G specimens from PNG were collected solely from Port Moresby, which is presumed to be the original invasion site for CRB-G within PNG. In the Solomon Islands, CRB-G was first identified in 2015, and all field collected samples included in the analysis presented by Marshall et al. 2017 were CRB-G. We do not dispute that Etebari et al. have found CRB individuals with the PNG haplotype on Guadalcanal, but we do not support their claim that this is evidence for a separate wave of invasion into the region (see next section for further discussion).
2) recent research to address new CRB invasions, particularly in Vanuatu and the Solomon Islands <br />
Etebari et al. report the presence of OrNV in CRB-S beetles collected from Efate, Vanuatu at some point between January and October 2019, but neither collection date nor specific locality are provided. These details are important because the presence of CRB-S was only confirmed in Vanuatu during June 2019. Our CRB-S samples collected from Mangaliliu, Efate, between June and September 2019 are negative for OrNV. In mid-September 2019, as part of the local eradication efforts against CRB, live OrNV was imported into Vanuatu. Bioassays were conducted to assess virus activity against the invasive CRB-S population and planned releases of OrNV were made on Efate in 2019 (Biosecurity Vanuatu, pers. comm.). Prior to the release of this preprint, we were unaware that these research activities in Vanuatu were likely to affect the conclusions drawn by Etebari and co-authors.
Etebari et al. also report the presence of CRB-S and the presence of OrNV on Guadalcanal, Solomon Islands in 2019. The sampling period is stated as between January and October 2019, but again neither collection date nor specific locality are provided. The authors state that ‘the OrNV now infecting O. rhinoceros in Solomon Islands arrived with an incursion of infected O. rhinoceros that originated in Southeast Asia’. We do not dispute the presence of CRB-S in the wider Honiara region of Guadalcanal in 2019, nor do we dispute the presence of virus in the same location and at the same time, because we have independent samples that confirm their presence in Honiara in 2019. There is, however, a simpler explanation for these findings. As part of the response to the CRB-G invasion into Honiara, screening of imported live OrNV isolates for virulence against CRB-G began in Honiara during 2016 (Marshall 2016). At the same time, CRB-S beetles were brought to Honiara from the Shortland Islands (Western Province, Solomon Islands) as part of the same project. There have been subsequent imports of live OrNV to Honiara for research purposes at intervals since 2016. It is likely that the presence of CRB-S and OrNV in Honiara is due to accidental release into the local environment. This does not support the invasion hypothesis suggested by Etebari and co-authors.
Furthermore, we note that our CRB samples from Russell Island (n = 3, Sept. 2019; n = 13, Feb. 2020; AgResearch 2020) were negative for OrNV, in contradiction to the results presented by Etebari et al. We concur with Etebari et al. that CRB populations in the New Georgia island group are negative for OrNV.
We agree with Etebari et al. that the effect of interbreeding between CRB-S and CRB-G on OrNV susceptibility requires further investigation, particularly in Honiara, where the two biotypes now occur together outside of their native range. Care needs to be taken, however, in the assessment of OrNV infection rates (see next section).
3) failure to prevent cross-contamination leading to artificially high ‘rates of OrNV infection’<br />
Etebari et al. present evidence of OrNV infection rates (%) based solely on PCR analysis of gut tissue samples. These tissue samples came from adult beetles captured in pheromone traps. From the information presented in the methods, it is unclear if sufficient precautions were taken to prevent accidental cross-contamination between beetles during the trapping process because the trap locations, length of time between trap set up and beetle collection, and beetle handling after collection are not described adequately. If an OrNV infected beetle is present in a trap among uninfected beetles, virus particles are easily transferred between individuals. This problem was documented by Ramle et al. 2005, who recommended careful handling of trapped beetles as a first step to minimise contamination risk. A tweet from the lead author of this preprint, dated 9 April 2019, includes a photo that shows strong potential for cross-contamination between beetles.
It is also unclear if the PCR protocol used by Etebari et al. included an appropriate dilution step to further reduce the risk of false positives because no details of the protocol are presented. Marshall et al. 2017 recommended a 1 in 5000 dilution to improve the accuracy of OrNV detection using PCR. Furthermore, care needs to be taken to avoid accidental contamination between samples during processing. A second tweet from the preprint’s lead author, dated 18 July 2019, includes a photo that shows strong potential for cross-contamination between samples in the laboratory.
Finally, it is common practice in insect pathology to use more than one indicator of infection, to reduce the risk of either false positives or false negatives (Lacey 2012; Vega and Kaya 2012). When assessing OrNV infection in CRB, this should include some combination of visual assessment of the gut at dissection, PCR analysis of gut tissue, preparation of histology samples to assess internal changes to the gut lining, and bioassays to determine viral virulence under controlled conditions. All of the OrNV infection rates presented by Etebari et al. are based on a single indicator, i.e. PCR analysis, with a high risk of cross-contamination, such that we consider the OrNV infection rates were overestimated significantly.
In conclusion, we cannot support the assertion of Etebari et al. that OrNV is widespread among new, invasive populations of CRB in the Pacific. Apart from Vanuatu, which was invaded recently by CRB-S without OrNV, the new wave of Pacific invasion is dominated by CRB-G populations without OrNV (Marshall et al. 2017; Reil et al. 2018).
References<br />
AgResearch (2020) Annex 1.1-Distribution map of CRB biotypes and virus. MFAT Progress Report WPG-0101699-DOC-4049125 (June 1, 2020).<br />
Huger AM. (2005) The Oryctes virus: Its detection, identification, and implementation in biological control of the coconut palm rhinoceros beetle, Oryctes rhinoceros (Coleoptera: Scarabaeidae). Journal of Invertebrate Pathology 89, 78-84. <br />
Lacey LA (2012) Manual of Techniques in Invertebrate Pathology (Second Edition), San Diego: Academic Press.<br />
Marshall SDG (2016) FAO Mission Report for Plant Production and Plant Protection TCP/S01/3501 – OTCP140014219: Use and production of Oryctes nudivirus to assist with control of the coconut rhinoceros beetle, Oryctes rhinoceros, in Solomon Islands (August 15, 2016).<br />
Marshall SDG, Moore A, Vaqalo M, Noble A & Jackson TA (2017) A new haplotype of the coconut rhinoceros beetle, Oryctes rhinoceros, has escaped biological control by Oryctes rhinoceros nudivirus and is invading Pacific Islands. Journal of Invertebrate Pathology 149, 127-134. <br />
Ramle M, Wahid MB, Norman K, Glare TR & Jackson TA (2005) The incidence and use of Oryctes virus for control of rhinoceros beetle in oil palm plantations in Malaysia. Journal of Invertebrate Pathology 89, 85-90. <br />
Reil JB, Doorenweerd C, San Jose M, Sim SB, Geib SM & Rubinoff D (2018) Transpacific coalescent pathways of coconut rhinoceros beetle biotypes: Resistance to biological control catalyses resurgence of an old pest. Molecular Ecology 27(22), 4459-4474. <br />
Vega FE & Kaya HK (2012) Insect Pathology (Elsevier Science).